The role of physical stability on the establishment of steady states in the phytoplankton community of two Maritime Antarctic lakes

Two Antarctic lakes near Hope Bay were studied during summers 1998 and 1999. One of the lakes (Boeckella) is located near Esperanza Station and exhibits a meso-eutrophic condition due to the input of nutrients of a nearby penguin rookery. Its surface generally remains ice-free during the Antarctic s...

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Autor principal: Allende, L.
Otros Autores: Izaguirre, I.
Formato: Capítulo de libro
Lenguaje:Inglés
Publicado: 2003
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100 1 |a Allende, L. 
245 1 4 |a The role of physical stability on the establishment of steady states in the phytoplankton community of two Maritime Antarctic lakes 
260 |c 2003 
270 1 0 |m Allende, L.; Fac. de Ciencias Exactas y Naturales, Depto. de Ecologia, Genet. y Evol., Universidad de Buenos Aires, (C1428 EHA), Buenos Aires, Argentina 
506 |2 openaire  |e Política editorial 
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520 3 |a Two Antarctic lakes near Hope Bay were studied during summers 1998 and 1999. One of the lakes (Boeckella) is located near Esperanza Station and exhibits a meso-eutrophic condition due to the input of nutrients of a nearby penguin rookery. Its surface generally remains ice-free during the Antarctic summer (December-March). The other lake (Chico) is situated on the Mount Flora shelf, is typically oligotrophic and its surface is ice-free only during brief periods in the summer season. The difference in the duration of the ice-cover insures that the wind mixes the former lake continuously throughout the summer, while the latter remains almost always stratified. X2, X3 and Z functional groups defined by Reynolds dominated phytoplankton in both lakes. In Lake Boeckella, Chlamydomonas spp. followed by Ochromonas sp. were the most frequently encountered taxa in the nano-phytoplankton fraction, however the latter species was dominant when the lake froze. In Lake Chico, the major contribution to this fraction was due to different genera of flagellated Chrysophyceae (Ochromonas sp., Chromulina spp., cf. Chrysidalis). In terms of density and biomass in both lakes picocyanobacteria represented a large proportion of the phytoplankton. Probably due to the typically low algal biodiversity of Antarctic lakes, both water bodies showed periods of more than 2 weeks when a maximum of only three species comprised more than 80% of the standing crop. In spite of this, Chico Lake was the only one in which no significant change was recorded in total biomass. Thus, we were able to identify equilibrium phases in the latter lake, which were confirmed by a low coefficient of variation. The presence of an almost permanent ice cover in Chico Lake generated more stable ecological conditions, allowing the development of steady state assemblages. On the contrary, the wind influence in the shallow Antarctic ice free lake (Lake Boeckella) provided continuous mixing events, disrupting the possibility of establishing a steady state.  |l eng 
536 |a Detalles de la financiación: Universidad de Buenos Aires, UBA 
536 |a Detalles de la financiación: Consejo Nacional de Investigaciones Científicas y Técnicas, CONICET 
536 |a Detalles de la financiación: Consejo Nacional de Investigaciones Científicas y Técnicas, CONICET 
536 |a Detalles de la financiación: Fondo para la Investigación Científica y Tecnológica, FonCyT 
536 |a Detalles de la financiación: This project was supported by grants of the “Agencia de Promociones Científicas y Técnicas” (FONCYT), and CONICET (Argentina). The Antarctic expeditions were supported by a cooperative project between Argentinean Antarctic Institute and the University of Buenos Aires. We also wish to thank the members of the Argentinean Esperanza Station for on site logistic support. 
593 |a Fac. de Ciencias Exactas y Naturales, Depto. de Ecologia, Genet. y Evol., Universidad de Buenos Aires, (C1428 EHA), Buenos Aires, Argentina 
690 1 0 |a ANTARCTIC LAKES 
690 1 0 |a FUNCTIONAL GROUPS 
690 1 0 |a PICOCYANOBACTERIA 
690 1 0 |a THERMAL PATTERNS 
690 1 0 |a BACTERIA 
690 1 0 |a BIODIVERSITY 
690 1 0 |a BIOMASS 
690 1 0 |a ECOLOGY 
690 1 0 |a LAKES 
690 1 0 |a PHASE EQUILIBRIA 
690 1 0 |a WIND 
690 1 0 |a WATER BODIES 
690 1 0 |a MARINE BIOLOGY 
690 1 0 |a COMMUNITY STRUCTURE 
690 1 0 |a ECOLOGICAL STABILITY 
690 1 0 |a FUNCTIONAL GROUP 
690 1 0 |a ICE COVER 
690 1 0 |a LAKE ECOSYSTEM 
690 1 0 |a PHYTOPLANKTON 
690 1 0 |a STEADY-STATE EQUILIBRIUM 
690 1 0 |a STRATIFICATION 
690 1 0 |a ANTARCTIC PENINSULA 
690 1 0 |a ANTARCTICA 
690 1 0 |a LAKE BOECKELLA 
690 1 0 |a LAKE CHICO 
690 1 0 |a WEST ANTARCTICA 
690 1 0 |a ALGAE 
690 1 0 |a BACTERIA (MICROORGANISMS) 
690 1 0 |a CHLAMYDOMONAS 
690 1 0 |a CHROMULINA 
690 1 0 |a CHRYSOPHYCEAE 
690 1 0 |a ESPERANZA 
690 1 0 |a OCHROMONAS 
690 1 0 |a SPHENISCIDAE 
700 1 |a Izaguirre, I. 
773 0 |d 2003  |g v. 502  |h pp. 211-224  |p Hydrobiologia  |x 00188158  |w (AR-BaUEN)CENRE-207  |t Hydrobiologia 
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